US20070114417A1 - Method for cross interference correction for correlation spectroscopy - Google Patents

Method for cross interference correction for correlation spectroscopy Download PDF

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US20070114417A1
US20070114417A1 US11/539,962 US53996206A US2007114417A1 US 20070114417 A1 US20070114417 A1 US 20070114417A1 US 53996206 A US53996206 A US 53996206A US 2007114417 A1 US2007114417 A1 US 2007114417A1
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wavelength
measurements
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signal
absorption
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James Hobby
Martin Lopez
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Servomex Group Ltd
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    • G—PHYSICS
    • G01—MEASURING; TESTING
    • G01N—INVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
    • G01N21/00—Investigating or analysing materials by the use of optical means, i.e. using sub-millimetre waves, infrared, visible or ultraviolet light
    • G01N21/17—Systems in which incident light is modified in accordance with the properties of the material investigated
    • G01N21/25—Colour; Spectral properties, i.e. comparison of effect of material on the light at two or more different wavelengths or wavelength bands
    • G01N21/31—Investigating relative effect of material at wavelengths characteristic of specific elements or molecules, e.g. atomic absorption spectrometry
    • G01N21/35—Investigating relative effect of material at wavelengths characteristic of specific elements or molecules, e.g. atomic absorption spectrometry using infrared light
    • G01N21/3504—Investigating relative effect of material at wavelengths characteristic of specific elements or molecules, e.g. atomic absorption spectrometry using infrared light for analysing gases, e.g. multi-gas analysis
    • G—PHYSICS
    • G01—MEASURING; TESTING
    • G01J—MEASUREMENT OF INTENSITY, VELOCITY, SPECTRAL CONTENT, POLARISATION, PHASE OR PULSE CHARACTERISTICS OF INFRARED, VISIBLE OR ULTRAVIOLET LIGHT; COLORIMETRY; RADIATION PYROMETRY
    • G01J3/00—Spectrometry; Spectrophotometry; Monochromators; Measuring colours
    • G01J3/28—Investigating the spectrum
    • G01J3/457—Correlation spectrometry, e.g. of the intensity
    • G—PHYSICS
    • G01—MEASURING; TESTING
    • G01N—INVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
    • G01N21/00—Investigating or analysing materials by the use of optical means, i.e. using sub-millimetre waves, infrared, visible or ultraviolet light
    • G01N21/17—Systems in which incident light is modified in accordance with the properties of the material investigated
    • G01N21/25—Colour; Spectral properties, i.e. comparison of effect of material on the light at two or more different wavelengths or wavelength bands
    • G01N21/27—Colour; Spectral properties, i.e. comparison of effect of material on the light at two or more different wavelengths or wavelength bands using photo-electric detection ; circuits for computing concentration
    • G01N21/274—Calibration, base line adjustment, drift correction
    • G—PHYSICS
    • G01—MEASURING; TESTING
    • G01N—INVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
    • G01N21/00—Investigating or analysing materials by the use of optical means, i.e. using sub-millimetre waves, infrared, visible or ultraviolet light
    • G01N21/17—Systems in which incident light is modified in accordance with the properties of the material investigated
    • G01N21/25—Colour; Spectral properties, i.e. comparison of effect of material on the light at two or more different wavelengths or wavelength bands
    • G01N21/31—Investigating relative effect of material at wavelengths characteristic of specific elements or molecules, e.g. atomic absorption spectrometry
    • G01N21/35—Investigating relative effect of material at wavelengths characteristic of specific elements or molecules, e.g. atomic absorption spectrometry using infrared light
    • G01N21/3504—Investigating relative effect of material at wavelengths characteristic of specific elements or molecules, e.g. atomic absorption spectrometry using infrared light for analysing gases, e.g. multi-gas analysis
    • G01N21/3518—Devices using gas filter correlation techniques; Devices using gas pressure modulation techniques
    • G—PHYSICS
    • G01—MEASURING; TESTING
    • G01N—INVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
    • G01N21/00—Investigating or analysing materials by the use of optical means, i.e. using sub-millimetre waves, infrared, visible or ultraviolet light
    • G01N21/17—Systems in which incident light is modified in accordance with the properties of the material investigated
    • G01N21/59—Transmissivity
    • G01N21/61—Non-dispersive gas analysers
    • G—PHYSICS
    • G01—MEASURING; TESTING
    • G01N—INVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
    • G01N21/00—Investigating or analysing materials by the use of optical means, i.e. using sub-millimetre waves, infrared, visible or ultraviolet light
    • G01N21/17—Systems in which incident light is modified in accordance with the properties of the material investigated
    • G01N21/25—Colour; Spectral properties, i.e. comparison of effect of material on the light at two or more different wavelengths or wavelength bands
    • G01N21/31—Investigating relative effect of material at wavelengths characteristic of specific elements or molecules, e.g. atomic absorption spectrometry
    • G01N21/35—Investigating relative effect of material at wavelengths characteristic of specific elements or molecules, e.g. atomic absorption spectrometry using infrared light
    • G01N21/37—Investigating relative effect of material at wavelengths characteristic of specific elements or molecules, e.g. atomic absorption spectrometry using infrared light using pneumatic detection

Definitions

  • the present invention relates to a method and apparatus for correcting or reducing cross interference in filter correlation and more particularly correction spectroscopy measurement.
  • Optical absorption measurements have long been used to measure the concentration of a component in a mixture.
  • the absorption behaviour can be described by the Beer-Lambert law.
  • a simple form of an absorption spectrometer consists of a light source, a means to select the relevant wavelength range, a sample chamber and detector. The reduction in the transmitted light intensity when the absorbing component is present allows the concentration of the component to be deduced. Whilst this may give sensitive readings for the component of interest, depending on the absorption strength and path length, it may be subject to zero and sensitivity errors due to changes in the source intensity and cross interference (measurement error) if other components are present which also absorb within the wavelength pass band.
  • Zero and sensitivity errors can occur because there is no reference to the change in intensity of the source with time. This effect can be compensated for by using a reference measurement which monitors the source output simultaneously with the measurement of interest.
  • the cross interference can be minimised by using a selective detection system, tuned to the specific absorption of the component of interest.
  • FIG. 1 Another approach is by using a single optical path gas filter correlation measurement.
  • light from a broad band source 1 is mechanically modulated using a wheel 2 containing a cuvette 3 filled with non-significantly absorbing gas, such as nitrogen and another cuvette 4 containing the gas of interest.
  • an optical band pass filter 5 is used to select a region of interest.
  • the resultant modulated emission is directed into a measurement cell 7 , where further absorption may occur, depending on the sample composition.
  • the signal is collected at an optical detector 8 where it is converted into an electrical signal, which is then processed by processing circuitry 9 to produce an external output signal.
  • the signal from the optical detector will consist of modulated output corresponding to the throughput from the different gas filled cuvettes.
  • the following will describe the simplified case of a single, non-absorbing cuvette filled with nitrogen and a single, absorbing cuvette filled with the gas of interest, in this case, NO (nitric oxide). Although this simple illustration is given, this description applies equally well to any material being measured by any spectroscopic technique such as using absorption or reflection.
  • FIGS. 2 a and b a schematic of the output signals is illustrated in FIGS. 2 a and b for the case of non-absorbing mixture (nitrogen) in the sample cell.
  • the signal which has gone through the NO cuvette will always have a smaller amplitude than the signal through the nitrogen cuvette, since some of the light corresponding to the absorption spectrum has been absorbed.
  • Different gains are applied to the two signals, by the processing circuitry 9 such that the magnitudes of the two signals are matched. This is taken as the zero point in deriving the concentration measurements.
  • FIGS. 2 c and d a change in the output signal occurs ( FIGS. 2 c and d ).
  • the change in the nitrogen cuvette signal is always larger than that of the NO cuvette, since the NO cuvette has already pre-absorbed a portion of the radiation corresponding to the NO absorption bands.
  • the amount of incident radiation absorbed by the NO cuvette will depend on, for example, its concentration, temperature, background gas and absorption path length.
  • the difference between the two gained signals, ⁇ I in FIG. 2 d is related to the NO concentration in the sample gas cell and so this sets the sensitivity for the measurement.
  • the difference is normally divided by the NO cuvette signal to give a normalised signal, which is independent of any changes in the source intensity and then multiplied by an instrumentation factor to give an NO concentration reading.
  • the effect of background interferent gas(es) can cause an error in the reading if they absorb within the pass band of the filter.
  • the example described above provides for two types of interference to occur: positive interference, which causes a positive error, where the interferent absorption coincides with an NO absorption bands and negative interference, which causes a negative error, where the absorption does not coincide with an absorption band. This is illustrated in FIG. 3 .
  • Positive interference results from an inherent inability to distinguish between NO and the interferent, but negative cross interference results from the normalised differential gain applied to the signals (i.e. proportional to (G ⁇ 1), where G is the normalised differential gain applied). Often both types of interference can occur simultaneously.
  • the magnitude of the cross interference for a particular gas mixture can be minimised through choice of the pass band of the optical filter and characteristics of the gas cuvettes. However, in some cases, such as with water as an interferent gas for NO, it may not possible to remove the interference satisfactorily, resulting in unacceptable error.
  • a common method of dealing with the effect of cross interference is to independently measure the concentration of the cross interferer, whether by gas filter correlation or other means, and correct accordingly. This, of course, requires extra equipment for a second measurement together with increased cost and complexity. Additionally, the sample would not be identical to that seen by the primary measurement, but could have temporal and/or spatial separation.
  • the present invention does not rely on a second measurement, but uses information already present in the signal. It intentionally varies the differential gain applied to the signals by changing the baseline reference in order to create an auto-correction function for the effect of background gases.
  • the positive cross interference is unaffected by any change in the baseline reference, since this is proportional to the relative strength of the absorption overlap of the interferent and NO absorption lines and hence taken out in the calibration.
  • the negative cross interference will be affected by the baseline reference, since this will change differential gain which needs to be applied.
  • FIG. 1 shows a diagrammatic representation of the basic apparatus for spectroscopic measurement
  • FIGS. 2 and 3 are diagrams aiding the explanation of a prior art method of using apparatus shown in FIG. 1 ;
  • FIGS. 4 and 7 are diagrams aiding the explanation of the preferred method according to the present invention.
  • the preferred embodiment utilises the same basic equipment as the prior art and this is shown in FIG. I and the operation is basically the same.
  • two or more baseline references i.e. two different gains
  • the degree of mismatch between the two signals when no interferent is present can be determined during calibration and any subsequent change in this mismatch gives a measurement of the background interferent concentration. This will hold true whether the interferent is present on its own, or in addition to NO.
  • This system can also be used for the correction for multiple cross interferents. This method presupposes that negative cross interference is always present. However, in reality, this will normally be the case, since two different compounds will not have the same spectral characteristics.
  • the concept is illustrated in simplified format in FIG. 4 .
  • the two systems 1 and 2 are both equally valid, although they have different gains G 1 and G 2 .
  • Each system can be calibrated independently to give a proportional response to the presence of NO in the sample cell. This is illustrated in FIG. 5 .
  • This method also applies if a change in the negative cross interference for NO itself in the sample cell occurs with respect to the NO in the sealed cuvette. This might happen, for example, due to line broadening such as that caused by changes in background gas composition and pressure or temperature changes. This would normally result in a measurement error due to a change in the relative NO sensitivity. However, using the method described in this patent, this effect could also be corrected for.

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Abstract

Correlation spectroscopy measure is improved by correcting for cross interference. This is achieved through applying different gains to the output signals whereby the effect of background interferent species can be calculated and an automatic correction factor applied.

Description

  • The present invention relates to a method and apparatus for correcting or reducing cross interference in filter correlation and more particularly correction spectroscopy measurement.
  • Optical absorption measurements have long been used to measure the concentration of a component in a mixture. The absorption behaviour can be described by the Beer-Lambert law. A simple form of an absorption spectrometer consists of a light source, a means to select the relevant wavelength range, a sample chamber and detector. The reduction in the transmitted light intensity when the absorbing component is present allows the concentration of the component to be deduced. Whilst this may give sensitive readings for the component of interest, depending on the absorption strength and path length, it may be subject to zero and sensitivity errors due to changes in the source intensity and cross interference (measurement error) if other components are present which also absorb within the wavelength pass band.
  • Zero and sensitivity errors can occur because there is no reference to the change in intensity of the source with time. This effect can be compensated for by using a reference measurement which monitors the source output simultaneously with the measurement of interest. The cross interference can be minimised by using a selective detection system, tuned to the specific absorption of the component of interest.
  • Another approach is by using a single optical path gas filter correlation measurement. The basic lay-out of which is illustrated in FIG. 1. In this method, light from a broad band source 1 is mechanically modulated using a wheel 2 containing a cuvette 3 filled with non-significantly absorbing gas, such as nitrogen and another cuvette 4 containing the gas of interest. In order to increase the signal to noise ratio, an optical band pass filter 5 is used to select a region of interest. The resultant modulated emission is directed into a measurement cell 7, where further absorption may occur, depending on the sample composition. The signal is collected at an optical detector 8 where it is converted into an electrical signal, which is then processed by processing circuitry 9 to produce an external output signal.
  • The signal from the optical detector will consist of modulated output corresponding to the throughput from the different gas filled cuvettes. The following will describe the simplified case of a single, non-absorbing cuvette filled with nitrogen and a single, absorbing cuvette filled with the gas of interest, in this case, NO (nitric oxide). Although this simple illustration is given, this description applies equally well to any material being measured by any spectroscopic technique such as using absorption or reflection.
  • Returning to our example, a schematic of the output signals is illustrated in FIGS. 2 a and b for the case of non-absorbing mixture (nitrogen) in the sample cell. The signal which has gone through the NO cuvette will always have a smaller amplitude than the signal through the nitrogen cuvette, since some of the light corresponding to the absorption spectrum has been absorbed. Different gains are applied to the two signals, by the processing circuitry 9 such that the magnitudes of the two signals are matched. This is taken as the zero point in deriving the concentration measurements.
  • Thereafter, when a sample containing the gas of interest is introduced to the sample cell, for example NO in a nitrogen background, a change in the output signal occurs (FIGS. 2 c and d). The change in the nitrogen cuvette signal is always larger than that of the NO cuvette, since the NO cuvette has already pre-absorbed a portion of the radiation corresponding to the NO absorption bands. The amount of incident radiation absorbed by the NO cuvette will depend on, for example, its concentration, temperature, background gas and absorption path length. The difference between the two gained signals, ΔI in FIG. 2 d, is related to the NO concentration in the sample gas cell and so this sets the sensitivity for the measurement. The difference is normally divided by the NO cuvette signal to give a normalised signal, which is independent of any changes in the source intensity and then multiplied by an instrumentation factor to give an NO concentration reading.
  • In the preceding example, the effect of background interferent gas(es) can cause an error in the reading if they absorb within the pass band of the filter. The example described above provides for two types of interference to occur: positive interference, which causes a positive error, where the interferent absorption coincides with an NO absorption bands and negative interference, which causes a negative error, where the absorption does not coincide with an absorption band. This is illustrated in FIG. 3. Positive interference results from an inherent inability to distinguish between NO and the interferent, but negative cross interference results from the normalised differential gain applied to the signals (i.e. proportional to (G−1), where G is the normalised differential gain applied). Often both types of interference can occur simultaneously.
  • The magnitude of the cross interference for a particular gas mixture can be minimised through choice of the pass band of the optical filter and characteristics of the gas cuvettes. However, in some cases, such as with water as an interferent gas for NO, it may not possible to remove the interference satisfactorily, resulting in unacceptable error.
  • A common method of dealing with the effect of cross interference is to independently measure the concentration of the cross interferer, whether by gas filter correlation or other means, and correct accordingly. This, of course, requires extra equipment for a second measurement together with increased cost and complexity. Additionally, the sample would not be identical to that seen by the primary measurement, but could have temporal and/or spatial separation.
  • The present invention does not rely on a second measurement, but uses information already present in the signal. It intentionally varies the differential gain applied to the signals by changing the baseline reference in order to create an auto-correction function for the effect of background gases. The positive cross interference is unaffected by any change in the baseline reference, since this is proportional to the relative strength of the absorption overlap of the interferent and NO absorption lines and hence taken out in the calibration. The negative cross interference, however, will be affected by the baseline reference, since this will change differential gain which needs to be applied.
  • In order that the present invention be more readily understood, an embodiment will now be described by way of example with reference to the accompanying drawings, in which:
  • FIG. 1. shows a diagrammatic representation of the basic apparatus for spectroscopic measurement;
  • FIGS. 2 and 3 are diagrams aiding the explanation of a prior art method of using apparatus shown in FIG. 1; and
  • FIGS. 4 and 7 are diagrams aiding the explanation of the preferred method according to the present invention.
  • The preferred embodiment utilises the same basic equipment as the prior art and this is shown in FIG. I and the operation is basically the same. However, if a measurement is taken simultaneously or sequentially using two or more baseline references (i.e. two different gains), then two different signals will result. The degree of mismatch between the two signals when no interferent is present can be determined during calibration and any subsequent change in this mismatch gives a measurement of the background interferent concentration. This will hold true whether the interferent is present on its own, or in addition to NO. This system can also be used for the correction for multiple cross interferents. This method presupposes that negative cross interference is always present. However, in reality, this will normally be the case, since two different compounds will not have the same spectral characteristics.
  • The concept is illustrated in simplified format in FIG. 4. For simplicity, it is assumed that the NO cuvette signal does not change significantly when NO is present in the cell due to pre-adsorption. The two systems 1 and 2 are both equally valid, although they have different gains G1 and G2. Each system can be calibrated independently to give a proportional response to the presence of NO in the sample cell. This is illustrated in FIG. 5.
  • When water is present, an error on the output is seen for both systems with gain G1 and G2. This is shown using experimental results in FIG. 6 for a constant level of 76 ppm NO in nitrogen for increasing levels of water background. Also shown in FIG. 6 is the corrected concentration readings using correction factors from a previous calibration with water (FIG. 7). The concentration of water can also be deduced from the difference in readings and hence a concentration reading could be displayed if required.
  • This method also applies if a change in the negative cross interference for NO itself in the sample cell occurs with respect to the NO in the sealed cuvette. This might happen, for example, due to line broadening such as that caused by changes in background gas composition and pressure or temperature changes. This would normally result in a measurement error due to a change in the relative NO sensitivity. However, using the method described in this patent, this effect could also be corrected for.

Claims (15)

1. A method for automatically compensating for the presence of a background interferent in a spectroscopic measurement of a material comprising analyzing an original measurement signal produced through the manipulation of artificially induced negative cross interferences in the signal.
2. A method for automatically compensating for the presence of spectral broadening in a spectroscopic measurement of a material comprising analyzing an original measurement signal produced through the manipulation of artificially induced negative cross interferences in the signal.
3. The method according to claim 1 further comprising taking measurements using two or more baseline references at different levels.
4. The method according to claim 3, wherein the two baseline references are achieved by altering the gain of processing circuitry,
5. The method as described in claim 1 further comprising using absorption measurements at any wavelength for any medium.
6. The method as described in claim 1 further comprising using reflectance measurements at any wavelength for any medium.
7. The method as described in claim 1 further comprising using emission measurements at any wavelength for any medium.
8. The method according to any one of the preceding claim 1 further comprising monitoring the presence of the said interferent and producing a signal relating to its concentration.
9. The method according to claim 2 further comprising monitoring the presence of spectral broadening and producing a signal relating to its cause, such as background gas composition, pressure or temperature.
10. The method according to claim 2 further comprising taking measurements using two or more baseline references at different levels.
11. The method according to claim 10 wherein the two baseline references are achieved by altering the gain of processing circuitry.
12. The method according to claim 2 further comprising using absorption measurements at any wavelength for any medium.
13. The method as described in claim 2 further comprising using reflectance measurements at any wavelength for any medium.
14. The method as described in claim 2 further comprising using emission measurements at any wavelength for any medium.
15. The method according to claim 2 further comprising monitoring the presence of the said inteferent and producing a signal relating to its concentration.
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US7943915B2 (en) * 2008-10-10 2011-05-17 Ge Infrastructure Sensing, Inc. Method of calibrating a wavelength-modulation spectroscopy apparatus
GB2524725B (en) * 2014-03-24 2016-03-30 Servomex Group Ltd Method and system for correcting incident light fluctuations in absorption spectroscopy
GB2524836A (en) * 2014-04-04 2015-10-07 Servomex Group Ltd Attachment and alignment device for optical sources, detectors and analysers, and modular analysis system
US10643008B2 (en) 2014-11-11 2020-05-05 Spectrasensors, Inc. Target analyte detection and quantification in sample gases with complex background compositions
GB2544507B (en) * 2015-11-18 2017-11-22 Servomex Group Ltd Method and system for reduction of influence of baseline distortion in absorption spectroscopy measurements

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US3488491A (en) * 1967-07-31 1970-01-06 Melpar Inc Filter techniques for gas analyzers employing an inert gas to pressure broaden the absorption spectrum of gas being detected
US3793525A (en) * 1973-01-02 1974-02-19 Philco Ford Corp Dual cell non-dispersive gas analyzer
US3811776A (en) * 1973-02-26 1974-05-21 Environmental Res & Tech Gas analyzer
US3904880A (en) * 1973-05-10 1975-09-09 Honeywell Inc Multi-component infrared analyzer

Family Cites Families (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
GB2113833B (en) * 1982-01-22 1985-02-06 Analytical Dev Company Limited Gas analysis apparatus and method of operation
FR2618554B1 (en) * 1987-07-22 1990-02-23 Moulene Daniel METHOD FOR THE OPTICAL ANALYSIS OF A GAS IN A GAS MIXTURE

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US3488491A (en) * 1967-07-31 1970-01-06 Melpar Inc Filter techniques for gas analyzers employing an inert gas to pressure broaden the absorption spectrum of gas being detected
US3793525A (en) * 1973-01-02 1974-02-19 Philco Ford Corp Dual cell non-dispersive gas analyzer
US3811776A (en) * 1973-02-26 1974-05-21 Environmental Res & Tech Gas analyzer
US3904880A (en) * 1973-05-10 1975-09-09 Honeywell Inc Multi-component infrared analyzer

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CN1971247B (en) 2011-06-29
GB0523817D0 (en) 2006-01-04
CN1971247A (en) 2007-05-30
US7751051B2 (en) 2010-07-06
EP1790971B1 (en) 2010-11-03
EP1790971A1 (en) 2007-05-30
ATE487125T1 (en) 2010-11-15
DE602006017955D1 (en) 2010-12-16
GB2429279B (en) 2008-08-06

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